Exercise set
Landfill Disposal, Leachate, Gas, and Airspace Exercises
Solved landfill engineering exercises for leachate storage, head control, airspace life, compaction, gas capture, flare downtime and release gates.
These exercises focus on landfill disposal controls rather than the whole solid-waste system. They cover leachate storage, treatment margin, head-on-liner, airspace life, compaction, daily cover, methane generation, gas collection, flare downtime, condensate, pump availability and release evidence.
Assume simplified screening calculations unless an exercise states otherwise. Field decisions require site permit limits, liner design, leachate head sensors, pump logs, settlement surveys, gas-header data, surface-emission scans, flare or engine records and corrective-action evidence.
Release Evidence Notes
Landfill evidence must preserve both mass and pathway. Waste tonnage affects airspace and gas; water balance affects leachate head and hauling; gas capture affects odor, explosion risk, greenhouse release and energy recovery.
Leachate evidence should state generation rate, storage volume, treatment or hauling capacity, starting inventory, pump status and head-on-liner margin. Wet-weather periods can control the decision even when annual averages look acceptable.
Gas evidence should state methane generation basis, collection efficiency, header capacity, condensate management, flare availability and surface-emission check results. A captured gas number is weak if downtime, bypass and wellfield balance are not shown.
Engineering Boundary Notes
These calculations do not replace landfill design, permit modeling, groundwater monitoring, gas migration review, surface-emission monitoring or closure engineering. They are screening exercises for disposal operations and release packages.
Common Release Mistakes
- using average leachate generation when the release decision is controlled by a storm week;
- counting gross airspace without daily cover, intermediate cover, settlement or unusable geometry;
- treating landfill gas power as proof of gas control without collection and flare evidence;
- ignoring condensate or header pressure limits that prevent gas collection;
- closing a release gate without matching tonnage, liquid, gas and inspection records.
Scenario Map
| Scenario | Exercises | Primary check | Engineering decision |
|---|---|---|---|
| Leachate control | 1, 2, 3, 14, 15 | storage, treatment, head, pump availability and hauling | Decide whether liquids control is credible. |
| Airspace and density | 4, 5, 6, 7, 16 | remaining life, compaction, cover use and settlement | Decide whether disposal capacity is defensible. |
| Gas control | 8, 9, 10, 11, 12, 13 | methane generation, collection headroom, flare downtime and emissions | Decide whether gas risk is controlled. |
| Release gate | 17, 18 | evidence completeness and all-of release | Decide whether the landfill package can close. |
Exercise 1: Wet-Weather Leachate Storage
A landfill cell generates 68\ \text{m}^3/\text{d} of leachate during a storm period. Treatment and hauling capacity is 45\ \text{m}^3/\text{d} for 5 days. Compute required temporary storage for the excess leachate.
Solution
Engineering Comment
At least 115\ \text{m}^3 of usable storage is needed before freeboard or contingency volume is added.
Plausibility Check
The excess is about one third of daily generation; over five days that gives a storage need a little above one hundred cubic meters.
Exercise 2: Leachate Treatment Capacity Margin
Average leachate flow is 52\ \text{m}^3/\text{d}. The treatment skid can process 70\ \text{m}^3/\text{d}. Compute the capacity margin.
Solution
Engineering Comment
A 34.6\% margin may be adequate for average operation, but storm inflow and pump downtime still need separate checks.
Plausibility Check
The spare capacity is 18\ \text{m}^3/\text{d}, roughly one third of the average load.
Exercise 3: Head-on-Liner Margin
Measured leachate head is 0.26\ \text{m}. The permit action level is 0.30\ \text{m}. Compute the remaining head margin.
Solution
Engineering Comment
Only 40\ \text{mm} remains. That is a narrow operating margin if the sensor uncertainty, pump cycling band or storm response is comparable.
Plausibility Check
The measured head is close to the limit, so the margin should be small.
Exercise 4: Remaining Landfill Airspace Life
Remaining permitted airspace is 420000\ \text{m}^3. Annual accepted waste is 150000\ \text{t/yr} and in-place density is 0.82\ \text{t/m}^3. Estimate remaining life, ignoring cover and settlement.
Solution
Annual volume consumed is:
Remaining life:
Engineering Comment
This is a gross screen. Daily cover, intermediate cover, slope geometry and settlement can change the usable life.
Plausibility Check
The site consumes almost 183000\ \text{m}^3 per year, so a little more than two years is reasonable.
Exercise 5: Compaction Density Improvement
Waste placement increases from 0.74 to 0.86\ \text{t/m}^3. For 120000\ \text{t/yr}, compute annual airspace saved.
Solution
Before improvement:
After improvement:
Engineering Comment
Compaction is an airspace control, not only an equipment productivity measure.
Plausibility Check
The density gain is material, so saving tens of thousands of cubic meters per year is plausible.
Exercise 6: Daily Cover Airspace Penalty
A cell receives 480\ \text{m}^3/\text{d} of compacted waste. Daily cover adds 12\% additional volume. Compute total daily airspace consumption.
Solution
Engineering Comment
Cover volume should be included in airspace accounting unless an approved alternative daily cover reduces the penalty.
Plausibility Check
A 12\% addition on about 500\ \text{m}^3/\text{d} should add about 60\ \text{m}^3/\text{d}.
Exercise 7: Diversion Effect on Cell Life
A cell has 250000\ \text{m}^3 of usable airspace. Baseline disposal is 95000\ \text{m}^3/\text{yr}. A diversion program reduces disposal by 14\%. Estimate new life.
Solution
New annual consumption:
Cell life:
Engineering Comment
Diversion should be credited only when residual mass and destination evidence are traceable.
Plausibility Check
Reducing annual consumption from 95000 to 81700\ \text{m}^3 stretches life from 2.63 to just over 3 years.
Exercise 8: Methane Generation Screen
Estimated landfill gas flow is 980\ \text{m}^3/\text{h} with 48\% methane. Compute methane flow.
Solution
Engineering Comment
The methane fraction matters for energy, flare temperature and explosion-risk evaluation.
Plausibility Check
About half of the total gas is methane, so methane flow should be close to 500\ \text{m}^3/\text{h}.
Exercise 9: Gas Collection Headroom
Measured landfill gas flow is 980\ \text{m}^3/\text{h}. The header fan can handle 1250\ \text{m}^3/\text{h}. Compute headroom.
Solution
Engineering Comment
Header headroom is useful only if individual wells, condensate traps and flare capacity can also accept the added flow.
Plausibility Check
The spare flow is 270\ \text{m}^3/\text{h}, a little over one quarter of the current flow.
Exercise 10: Flare Downtime Methane Venting
During a flare outage, 470\ \text{m}^3/\text{h} of methane is not destroyed for 6 hours. Estimate the undestroyed methane volume.
Solution
Engineering Comment
The release record should distinguish planned outage, emergency outage, bypass route and whether gas was routed to another control device.
Plausibility Check
Several hundred cubic meters per hour over several hours gives several thousand cubic meters.
Exercise 11: Condensate Knockout Capacity
A gas header produces 0.18\ \text{m}^3/\text{h} of condensate. The knockout pot has 1.2\ \text{m}^3 of usable volume. Estimate time to fill if drainage is blocked.
Solution
Engineering Comment
Condensate can become the limiting gas-control failure mode even when fan capacity looks adequate.
Plausibility Check
At less than a quarter cubic meter per hour, a one cubic meter vessel fills over several hours, not minutes.
Exercise 12: Landfill Gas Engine Power
Captured methane energy input is 4.7\ \text{MW}_{th}. Engine electrical efficiency is 34\%. Compute electrical output.
Solution
Engineering Comment
Electrical output is not gas-control proof. A flare or backup path is still needed when the engine is unavailable.
Plausibility Check
One third of about 5\ \text{MW}_{th} is about 1.7\ \text{MW}.
Exercise 13: Surface Emission Exceedance Rate
A surface-emission scan checks 160 points. Twelve points exceed the action level. Compute exceedance rate.
Solution
Engineering Comment
The rate should trigger wellfield adjustment and cover inspection if it exceeds the site’s operating criterion.
Plausibility Check
Twelve out of one hundred sixty is less than one tenth, so 7.5\% is plausible.
Exercise 14: Leachate Pump Availability
Two leachate pumps are arranged one duty and one standby. Each pump availability is 0.93. Estimate availability of at least one pump, assuming independent failures.
Solution
Probability both fail:
Availability of at least one pump:
Engineering Comment
Independence is a strong assumption. Shared power, level controls and clogged sumps can defeat redundancy.
Plausibility Check
Two standby-capable pumps should be much more available than one pump if failures are independent.
Exercise 15: Leachate Hauling Slot Check
Excess leachate is 115\ \text{m}^3. Each tanker carries 23\ \text{m}^3. Compute required tanker loads.
Solution
Engineering Comment
The calculation closes only if the receiving plant, access road and loading station can support the five trips in the required window.
Plausibility Check
Five equal tankers at 23\ \text{m}^3 each exactly remove 115\ \text{m}^3.
Exercise 16: Settlement Airspace Gain
Surveyed settlement creates 18000\ \text{m}^3 of additional apparent airspace. If only 70\% is usable because of grading constraints, compute usable gain.
Solution
Engineering Comment
Settlement should be reconciled with grades, stormwater controls and final cover requirements before being counted as disposal capacity.
Plausibility Check
Seventy percent of 18000 is a little over 12000\ \text{m}^3.
Exercise 17: Landfill Evidence Closure Score
A landfill release checklist has 8 required evidence items: leachate generation, storage, head trend, pump status, airspace survey, waste tonnage, gas collection and surface-emission scan. Six are complete. Compute completion.
Solution
Engineering Comment
A 75\% record is not release-ready if the missing items are pathway controls such as head trend or gas scan.
Plausibility Check
Six of eight items is three quarters.
Exercise 18: Landfill Release Gate
A release gate requires: leachate head below action level, storage margin above 100\ \text{m}^3, gas collection headroom above 20\%, no unresolved surface-emission action, and evidence completion at least 90\%. Current values are 0.26\ \text{m} versus 0.30\ \text{m} action level, 115\ \text{m}^3 storage margin, 27.6\% gas headroom, one unresolved surface-emission action and 75\% evidence completion. Decide release status.
Solution
Head passes, storage passes and gas headroom passes. Surface-emission action fails, and evidence completion fails:
Release status:
Engineering Comment
The correct decision is to hold release. Passing hydraulic and gas-capacity numbers does not close unresolved field evidence.
Plausibility Check
An all-of gate fails when any required condition fails; here two conditions fail.
Validation Package Checklist
- Leachate generation, storage, treatment or hauling capacity, head trend and pump status are on the same time basis.
- Airspace calculations include density, cover, settlement, survey limits and usable geometry.
- Gas calculations include methane fraction, collection capacity, flare or engine availability, condensate and surface checks.
- Release decisions preserve unresolved corrective actions instead of hiding them inside average performance.